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International Research Journal     ISSN-0975-3486       VOL. I * ISSUE—3&4         RNI : RAJBIL/2009/30097

                           Research Paper—Botany & Microbiology
                               STUDIES ON PHYTOPLANKTON
                               DIVERSITY OF POLSAYPARA &
                              DEEPAK NAGAR POND OF DURG
                                  CITY; DISTT. DURG (C.G.)
 Dec.-09—Jan.-2010

                                      *G. S. Thakur**Nishant Meshram
                                      ***Devendra Kumar
*_**_***Dept. of Botany & Microbiology, Govt. V. Y. T. PG.Autonomous College Durg
 ABSTRACT
   Phytoplankton are common inhabitants of surface water and pioneer of an aquatic food chain. The
   phytoplankton has great significance in the biology of the creek as they provide food for the organisms,
   especially for Zooplankton. The present investigation is an attempt to study the phytoplankton
   community & physicochemical parameters in two ponds (Polsaypara & Deepak Nagar) of Durg city
   area” district Durg. During the study the total number of phytoplankton were counted. Total 28
   phytoplankton species were recorded in Polsaypara pond, and 24 phytoplankton species were
   recorded in Deepak Nagar pond. The high temperature & pH favors the growth of cyanobacteria &
   chlorophyceae group of phytoplankton.
Key word: Physicochemical parameters, ponds, phytoplankton.
Introduction                                             quality. The number of workers such as Saxena (1982);
     The Phytoplankton study is a very useful tool for   Malhotra (1988) studied the composition and seasonal
the assessment of water quality in any type of water     abundance of phytoplankton in Tropical fresh water
and also contributes to an understanding of the basic    pond at Aligarh. Many workers have published their
nature and general economy of the pond. Number and       work on aquatic environment and ecology of
kinds of phytoplankton grow in surface waters depend     phytoplankton in fresh water Khan (1992), Yogesh
on environmental conditions. Sewage and organic          Shastry etal. (1999), Dwivedi and Pandey (2002), More
waste water increase the productivity of the waters      and Nandon (2003). Water is an important ecological
and their crops of algae and other plankton organisms.   factor and universal solvent too. It also maintains many
Phytoplankton being the primary producer from the        physiological activities of living organisms. It is most
lowest tropic level in the food chain of fresh water     important natural resource and we depend on water
ecosystem and play a key role in fish culture.           for irrigation, industry and domestic needs.
According to Gerlach (1975) they produce 360 gm               The present study has been undertaken to study
organically bound carbon in a year per square meter.     the phytoplankton population and characteristics of
The number and species of phytoplankton serves to        water in two ponds of Durg city. Durg generally has a
determine the quality of water body. The structure of    dry tropical weather which is moderate but on a warmer
aquatic community is important in monitoring the         side in summer season. The peak temperature usually

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International Research Journal     ISSN-0975-3486        VOL. I * ISSUE—3 &4         RNI : RAJBIL/2009/30097
reached in May / June and can be as high as 45º           bottom while the hole was inserted a shorter tube that
centigrade. The onset monsoon usually from July and       ended near the mouth. The neck of the bottle was tied
the season extends up to September with monsoon           with a nylon thread. The samples were collected by air
peaking during July and August, Durg district (20º 23’    replacement principle. Phytoplankton were collected
- 22º 02’ N latitude, and 80º 46’- 81º 58’ E Longitude)   from two ponds (P1 & P2) between 9 to 10 am with the
occupies geographical area of 8701.8 sq KM. and rich      help of phytoplankton net, and 25ml of 4%
in mineral resources.                                     formaldehyde was added (Welch 1948) and
Materials and Methods                                     sedimentation was done.
        Sampling - Stagnant surface water sample for           The sediments were finally reduced to 20 ml by
physico - chemical analysis were collected from two       centrifugation and were preserved in glass vial. The
ponds (Polsaypara pond P1 & Deepak Nagar pond P2)         identification was done up to generic level as described
during study period (January, February and March          by Fritsch (1979) and Desikachary (1959). The water
2009) between 9 to 10 am with the help of sampler         temperature, pH, & Dissolved Oxygen (DO) were
designed by us. The sampler was made up of a thick        determined at sampling sites while Turbidity, Total
walled glass bottle of one liter capacity. The rubber     Solid, Conductivity, Phosphates and Bio - chemical
stopper was having two holes, one inserted with a         oxygen demand (BOD) were determined in the
long tube one end of which was almost touching the        laboratory. (APHA, 1985 and Trivedi & Goel, 1986).
                                        Table—1 (Polsaypara Pond P1)
 PHYSICO - CHEMICAL PARAMETERS                              JAN           FEB              MARCH
 Temperature (º C )                                         20.1          25.0             27.0
 pH                                                         9.05          9.38             9.65
 Conductivity(µmhos)                                        0.25          0.26             0.24
 Total dissolved solids(mg/l)                               70            70               80
 Turbidity (NTU)                                            42.0          48.8             46.5
 Phosphate (mg/l)                                           5.24          5.11             4.17
 Dissolved Oxygen(mg/l)                                     7.28          10.3             8.39
 Bio-chemical Oxygen Demand (mg/l)                          5.7           4.6              4.3




122
International Research Journal   ISSN-0975-3486      VOL. I * ISSUE—3&4    RNI : RAJBIL/2009/30097




Serial No.   Occurred Phytoplankton                                   Jan       Feb       March
Group        Chlorophyceae
1            Chlamydomonas globosa                                     +         +          +
2            Gonium compactum Iyenger                                  +         -          +
3            Pandorina morum (Mull) Bory                               +         -          +
4            Pediastrum simplex Meyen                                  +         +          +
5            Chlorella vulgaris Beijerinck                             +         +          +
6            Volvox globater                                           +         -          -
7            Tetraedron muticum A. (Braun)Hansgirg                     +         +          -
8            Oocystis ecballocystiformis Iyanger                       +         -          +
9            Scencdesmus armatus G.M.Smith                             +         +          +
10           Senedesmus var.bogalariensis G.M.Smith                    +         +          +
11           Senedesmus dimorphus (Terpi) kuetz                        +         +          +
Group        Bacillariophyceae
12           Navicula grimmii Krasske                                  +         +          +
13           Nitzschia palea(Kutz) W.Sm.                               +         +          +
14           Primularia interrupta W.Sm. Forma subcapitata Fritsch     +         -          -
15           Fragilaria pinnata Ehr                                    +         +          +
16           Cyclotella catenata Brun                                  +         +          +
17           Melosira granulate (Ehr)Ralfs                             +         -          +
18           Coscinodiscus                                             +         +          +
19           Sysendra rumpens Kutz.                                    -         +          +
20           Gomphonema lanceolatum Ehr                                +         -          -
Group        Myxophyceae
21           Arthrospira platensis(Nordst)Gom.                         +         +          +

çÚUâ¿ü °ÙæçÜçââ °‡ÇU §ßñËØé°àæÙ                                                                 123
International Research Journal   ISSN-0975-3486     VOL. I * ISSUE—3 &4    RNI : RAJBIL/2009/30097
             Spirulina labirinthiformis Gom.                           -         +            +
23           Phormidium ambiguum Gom.                                  -         +            -
24           Anabaena utermohlii Geitler                               -         +            +
25           Anabaenopsis circularis Wolosz.                           -         +            -
Group        Euglenophyceae
26           Euglena proxima Dangeard                                  -         +            +
27           Trachelomona scylindrica Ehr                              -         +            +
28           Strombomonas ovalis (Playf) Defl                          -         +            +
                                    Table-4 Deepak Nagar Pond T2
S No.        Occurred Phytoplankton                                   Jan       Feb      March
Group        Chlorophyceae
1            Chlamydomonas globosa                                     +         +            +
2            Gonium compactum Iyenger                                  +         +        +
3            Pandorina morum (Mull) Bory                               +         +        +
4            Pediastrum simplex Meyen                                  +         +        +
5            Chlorella vulgaris Beijerinck                             +         -        +
6            Volvox globater                                           -         -        +
7            Tetraedron muticum A. (Braun)Hansgirg                     +         +        +
8            Closterium cynthica De.Not.Var.jenneri Kriger             +         +        +
9            Scenedesmus armatus G.M.Smith                             +         +        +
Group        Bacillariophyceae
10           Nitzschia palea(Kutz) W.Sm                                +         +        -
11           Primularia interrupta W.Sm. Forma subcapitata Fritsch     -         +        +
12           Fragilaria pinnata Ehr                                    +         +        +
14           Cyclotella catenata Brun                                  +         +        +
15           Melosira granulate (Ehr)Ralfs                             +         -        +
16           Coscinodiscus                                             +         +        +
Group        Myxophyceae
17           Spirulina labirinthiformis Gom.                           +         +        +
18           Arthospira platensis(Nordst)Gom.                          +         +        -
19           Phormidium ambiguum Gom.                                  +         +        -
20           Anabaena utermohlii Geitler                               +         +        +
21           Anabaenopsis circularis Wolosz.                           +         +        -
Group        Euglenophuceae
22           Phacus cylindraceus Popova                                +         +        +
23           Euglena caudate Huebner                                   +         +        -
24           Trachelomonas cylindrical Ehr.                            +         +        +




124
International Research Journal       ISSN-0975-3486       VOL. I * ISSUE—3&4         RNI : RAJBIL/2009/30097

   Images taken by Phase-Contrast Microscope for identification




Result & Discussion                                        temperature and pH, whereas, Mary Bai (1989) reported
   Physico - chemical parameter                            that the pH of polluted water fluctuates in the range of
     The result of Physico - chemical parameters and       8 to 9. The pH value of P1 was near about same the
the phytoplankton study of the surface water of two        result of Mary Bai. The alkaline pH and reduced water
ponds are presented in tables 1, 2, 3 & 4 for              level supports the dominance of cyanobacterial species
convenience of discussion. The ponds were                  due to increased photosynthesis activity.
represented by P1 (Polsaypara pond) and P2 (Deepak              Conductivity of P1 range from 0.88 to1.22 µmhos
Nagar pond). Water temperature of P1 were recorded         and P2 range from 0.24 to 0.26 µmhos were recorded;
ranging from 20.1ºC to 23.1ºC during study period          higher value in P2 than P1. Turbidity (NTU) & Total
(Table -1); whereas the temperature of P2 (table 2) were   Dissolved Solid value was higher in P1 than P2. The
recorded ranging from 20.3ºC to 27.2ºC (Table -2).         high content of total dissolved solids elevates the
Comparatively higher temperature of P2 was due to          density of water and such a medium increases
the protected by all sides. This high range of             osmoregulatory stress on aquatic biota (Verma et al
temperature favors the grow of phytoplankton life.         1978). The value of phosphates ranged between 4.17
     The pH value of P1 range from 8.63 to 9.25. It was    to 5.24mg/l in P2 and 5.44 to 6.35mg/l in P1. It was
minimum (8.63) in the month of January and maximum         higher value than P2. The higher phosphate value of
(9.25) during March 2009. Whereas pH of P2 range           P1 could possibly be due to sewage pollution and
from 9.05 to 9.65. It was minimum (9.05) in month of       human interfere by washing clothes and bathing.
January and maximum (9.65) in March. Singhai (1986)        Dissolved oxygen in P1 was ranged from 3.3 to 4.2 mg/
has obtained a direct relationship between water           l whereas in P2 was ranged from 7.28 to 10.31mg/l. It
çÚUâ¿ü °ÙæçÜçââ °‡ÇU §ßñËØé°àæÙ                                                                              125
International Research Journal          ISSN-0975-3486          VOL. I * ISSUE—3 &4            RNI : RAJBIL/2009/30097
was high in P2. The dissolved oxygen almost all plants           species Chlamydomonas, Pediastrum, Closterium,
and animals need for respiration. Low dissolved                  Scenedesmus with maximum while Gonium, Pandorina,
oxygen creates favorable condition for phytoplankton             Tetraedron with minimum occurrence. Chlorella,
growth. Biological Oxygen Demand value was recorded              Volvox, Oocystis and Ankistrodesmus species were
range from 30.4 to 37.4 mg/l in P1 and in P2 it was range        recorded occasionally. Among Diatoms Navicula,
from 4.3 to 5.7mg/l. This value indicated that the               Nitgschila, Fragilaria, Cyndrella, Syrendra,
Polsaypara pond (P1) is more polluted than the Deepak            Melosira,Gomphonella & Cyclotella species showed
Nagar pond (P2).The change in physicochemical                    maximum density. Among Cyanobactera population,
parameters also influence water bodies as it is observed         five species namely Arthospira, spirulina were
in the present study.                                            recorded maximum density while Phormidium,
Phytoplankton composition                                        anabaena anabaenopsis with less frequency and
     At pond P1 the total number of 26 species of                density. Group Euglenophyceae was represented by
phytoplankton consisting of 9 species of                         Euglena and Tracholemons with maximum occurrence.
Chlorophyceae, 9 species of Bacillariophyceae, 5                     Deepak Nagar Pond: - Group Chlorophyceae
species of Myxophyceae and 2 species of                          included species Chlamydomonas, Pediastrum,
Euglenophyceae were identified (Table no. 1). At pond            Closterium, Scenedesmus, Pandorina with maximum
P2 the total number of 24 species comprising of 6                while Gonium, Tetraedron, Chlorella, Volvox Oocystis
species of diatoms, 9 species of Chlorophyceae 5                 species were recorded with minimum occurrence.
species of Myxophyceae and 3 species of                          Among diatoms Navicula, Nitzschia & Fragilaria
Eulenophyceae and were recorded. At pond P2                      species showed maximum density. Among
Diatoms were dominated species. Phytoplankton                    cyanobacterial population Spirulina, & Arthospira
population among diatoms such as Cyclotella,                     were found with maximum density followed by
Melosira & Coscinodiscus were found as most                      Phormidum, Anabaena and Anabaenopsis. Group
dominated species.                                               Euglenoidae was represented by Phacus, Euglena and
     Polsaypara pond: - Group Chlorophyceae included             Trachetomonas species.

R E F E R E N C E
      • APHA (1985) Standard methods of the estimation of water, sewage and industrial waste APHA, AWWA, Washington. •
Chakrabarty R.O, Roy P and Singh, S.P. (1959) A quantitative study of plankton and the physico- chemical condition of the
river Yamuna at Allahabad in 1954-55, Indian J. fish. 6: 186- 203.            • Desikachary T.V. (1959) Cyanophyta ICAR,
Publication. New Delhi, • Dwivedi B.K. and G.C. Pandey (2002) Physico- chemical factors and algal diversity of two ponds
Faizabad India Poll. Res. 21(3): 361-370. • Fritsch, F.E. (1979) The structure and reproduction of the algae. Vikas publishing
house Pvt. Ltd. • George, M.G. (1966) Comparative plankton Ecology of five fresh water fish tank in Delhi India. Hydrobiologia.
27: 81-108. • Gleason H.A. (1922) On the relation between species and area Ecology vol.3:156-162 • Goel, P. K., B. gopal R.K.
Trivedi (1980) Impact of sewage on fresh water ecosystem. General features of water bodies and sewage Int. J, Ecol. Vol.
17:39:44. • Khan, A. M. (1992) Pysico – chemical characteristics of vishnupuri dam water with special reference to plankton,
Ph.D. Thesis, Marathwada University, Aurangabad. • Joseph, J., P N K Nambisan, C. S. Shynamma and P.T. Lakshmanan (1984)
Studies on Phytoplankton in polluted waters. J. Mar, Biol. Ass. India Vol. 26 (1&2): 42-46. • Mary Bai, M. (1989) Pollution in
polar river physico – chemical parameters in environmental impact on biosynthesis, Eds Proceeding (Vol. 2) of the 10 th annual
seminar on Environmental Impact on Biosynthesis at Loyala college, Madras, India. • More Y.S. and Nandan (2003) Hydrobiological
study of algae of panzara dam Maharastra Eco. Env. and cons. 9{3) 367-369. • Singhai, S. (1956) Hydrological and ecological
studies of newly made Tawa reservoir at Ranipur, Ph.D. Thesis, H.S. Gaur University, Sagar • Sinha Sunju, Naik M.L. (1997)
Phytoplanktons and macrophytes in the ponds of Raipur city area.Gupta Offset, Bajrang Nagar; Raipur. • Subrahmanyum,
M.N.V. and P.V. Bhavanarayana (1989) Distribution and abundance of phytoplankton in Visankhapatnam harbour Indian J.
mar. Sci, Vol, 18: 251-258. • Yoggesh, Shastri, Bharat V. P. and Bhogaonkar (1999) Hydrobiological studies of a Pescolation
tank II Algal flora. J. Aqua. Biol. Vol. 14 (1&2) : 1-2. • Trivedi R..K. and P.K. Goel (1986) Chemical and Biological methods
for water pollution studies. Environmental Publication. Karad. • Verma, S.R., Tyagi A. R. and Dalella R.C. (1978) Physico –
chemical and biological characteristics of Karadabad drain in U.P. Indian J. Environment Health; 20(1) : 1- 13.

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Phytoplankton diversity of two ponds in Durg, India

  • 1. International Research Journal ISSN-0975-3486 VOL. I * ISSUE—3&4 RNI : RAJBIL/2009/30097 Research Paper—Botany & Microbiology STUDIES ON PHYTOPLANKTON DIVERSITY OF POLSAYPARA & DEEPAK NAGAR POND OF DURG CITY; DISTT. DURG (C.G.) Dec.-09—Jan.-2010 *G. S. Thakur**Nishant Meshram ***Devendra Kumar *_**_***Dept. of Botany & Microbiology, Govt. V. Y. T. PG.Autonomous College Durg ABSTRACT Phytoplankton are common inhabitants of surface water and pioneer of an aquatic food chain. The phytoplankton has great significance in the biology of the creek as they provide food for the organisms, especially for Zooplankton. The present investigation is an attempt to study the phytoplankton community & physicochemical parameters in two ponds (Polsaypara & Deepak Nagar) of Durg city area” district Durg. During the study the total number of phytoplankton were counted. Total 28 phytoplankton species were recorded in Polsaypara pond, and 24 phytoplankton species were recorded in Deepak Nagar pond. The high temperature & pH favors the growth of cyanobacteria & chlorophyceae group of phytoplankton. Key word: Physicochemical parameters, ponds, phytoplankton. Introduction quality. The number of workers such as Saxena (1982); The Phytoplankton study is a very useful tool for Malhotra (1988) studied the composition and seasonal the assessment of water quality in any type of water abundance of phytoplankton in Tropical fresh water and also contributes to an understanding of the basic pond at Aligarh. Many workers have published their nature and general economy of the pond. Number and work on aquatic environment and ecology of kinds of phytoplankton grow in surface waters depend phytoplankton in fresh water Khan (1992), Yogesh on environmental conditions. Sewage and organic Shastry etal. (1999), Dwivedi and Pandey (2002), More waste water increase the productivity of the waters and Nandon (2003). Water is an important ecological and their crops of algae and other plankton organisms. factor and universal solvent too. It also maintains many Phytoplankton being the primary producer from the physiological activities of living organisms. It is most lowest tropic level in the food chain of fresh water important natural resource and we depend on water ecosystem and play a key role in fish culture. for irrigation, industry and domestic needs. According to Gerlach (1975) they produce 360 gm The present study has been undertaken to study organically bound carbon in a year per square meter. the phytoplankton population and characteristics of The number and species of phytoplankton serves to water in two ponds of Durg city. Durg generally has a determine the quality of water body. The structure of dry tropical weather which is moderate but on a warmer aquatic community is important in monitoring the side in summer season. The peak temperature usually çÚUâ¿ü °ÙæçÜçââ °‡ÇU §ßñËØé°àæÙ 121
  • 2. International Research Journal ISSN-0975-3486 VOL. I * ISSUE—3 &4 RNI : RAJBIL/2009/30097 reached in May / June and can be as high as 45º bottom while the hole was inserted a shorter tube that centigrade. The onset monsoon usually from July and ended near the mouth. The neck of the bottle was tied the season extends up to September with monsoon with a nylon thread. The samples were collected by air peaking during July and August, Durg district (20º 23’ replacement principle. Phytoplankton were collected - 22º 02’ N latitude, and 80º 46’- 81º 58’ E Longitude) from two ponds (P1 & P2) between 9 to 10 am with the occupies geographical area of 8701.8 sq KM. and rich help of phytoplankton net, and 25ml of 4% in mineral resources. formaldehyde was added (Welch 1948) and Materials and Methods sedimentation was done. Sampling - Stagnant surface water sample for The sediments were finally reduced to 20 ml by physico - chemical analysis were collected from two centrifugation and were preserved in glass vial. The ponds (Polsaypara pond P1 & Deepak Nagar pond P2) identification was done up to generic level as described during study period (January, February and March by Fritsch (1979) and Desikachary (1959). The water 2009) between 9 to 10 am with the help of sampler temperature, pH, & Dissolved Oxygen (DO) were designed by us. The sampler was made up of a thick determined at sampling sites while Turbidity, Total walled glass bottle of one liter capacity. The rubber Solid, Conductivity, Phosphates and Bio - chemical stopper was having two holes, one inserted with a oxygen demand (BOD) were determined in the long tube one end of which was almost touching the laboratory. (APHA, 1985 and Trivedi & Goel, 1986). Table—1 (Polsaypara Pond P1) PHYSICO - CHEMICAL PARAMETERS JAN FEB MARCH Temperature (º C ) 20.1 25.0 27.0 pH 9.05 9.38 9.65 Conductivity(µmhos) 0.25 0.26 0.24 Total dissolved solids(mg/l) 70 70 80 Turbidity (NTU) 42.0 48.8 46.5 Phosphate (mg/l) 5.24 5.11 4.17 Dissolved Oxygen(mg/l) 7.28 10.3 8.39 Bio-chemical Oxygen Demand (mg/l) 5.7 4.6 4.3 122
  • 3. International Research Journal ISSN-0975-3486 VOL. I * ISSUE—3&4 RNI : RAJBIL/2009/30097 Serial No. Occurred Phytoplankton Jan Feb March Group Chlorophyceae 1 Chlamydomonas globosa + + + 2 Gonium compactum Iyenger + - + 3 Pandorina morum (Mull) Bory + - + 4 Pediastrum simplex Meyen + + + 5 Chlorella vulgaris Beijerinck + + + 6 Volvox globater + - - 7 Tetraedron muticum A. (Braun)Hansgirg + + - 8 Oocystis ecballocystiformis Iyanger + - + 9 Scencdesmus armatus G.M.Smith + + + 10 Senedesmus var.bogalariensis G.M.Smith + + + 11 Senedesmus dimorphus (Terpi) kuetz + + + Group Bacillariophyceae 12 Navicula grimmii Krasske + + + 13 Nitzschia palea(Kutz) W.Sm. + + + 14 Primularia interrupta W.Sm. Forma subcapitata Fritsch + - - 15 Fragilaria pinnata Ehr + + + 16 Cyclotella catenata Brun + + + 17 Melosira granulate (Ehr)Ralfs + - + 18 Coscinodiscus + + + 19 Sysendra rumpens Kutz. - + + 20 Gomphonema lanceolatum Ehr + - - Group Myxophyceae 21 Arthrospira platensis(Nordst)Gom. + + + çÚUâ¿ü °ÙæçÜçââ °‡ÇU §ßñËØé°àæÙ 123
  • 4. International Research Journal ISSN-0975-3486 VOL. I * ISSUE—3 &4 RNI : RAJBIL/2009/30097 Spirulina labirinthiformis Gom. - + + 23 Phormidium ambiguum Gom. - + - 24 Anabaena utermohlii Geitler - + + 25 Anabaenopsis circularis Wolosz. - + - Group Euglenophyceae 26 Euglena proxima Dangeard - + + 27 Trachelomona scylindrica Ehr - + + 28 Strombomonas ovalis (Playf) Defl - + + Table-4 Deepak Nagar Pond T2 S No. Occurred Phytoplankton Jan Feb March Group Chlorophyceae 1 Chlamydomonas globosa + + + 2 Gonium compactum Iyenger + + + 3 Pandorina morum (Mull) Bory + + + 4 Pediastrum simplex Meyen + + + 5 Chlorella vulgaris Beijerinck + - + 6 Volvox globater - - + 7 Tetraedron muticum A. (Braun)Hansgirg + + + 8 Closterium cynthica De.Not.Var.jenneri Kriger + + + 9 Scenedesmus armatus G.M.Smith + + + Group Bacillariophyceae 10 Nitzschia palea(Kutz) W.Sm + + - 11 Primularia interrupta W.Sm. Forma subcapitata Fritsch - + + 12 Fragilaria pinnata Ehr + + + 14 Cyclotella catenata Brun + + + 15 Melosira granulate (Ehr)Ralfs + - + 16 Coscinodiscus + + + Group Myxophyceae 17 Spirulina labirinthiformis Gom. + + + 18 Arthospira platensis(Nordst)Gom. + + - 19 Phormidium ambiguum Gom. + + - 20 Anabaena utermohlii Geitler + + + 21 Anabaenopsis circularis Wolosz. + + - Group Euglenophuceae 22 Phacus cylindraceus Popova + + + 23 Euglena caudate Huebner + + - 24 Trachelomonas cylindrical Ehr. + + + 124
  • 5. International Research Journal ISSN-0975-3486 VOL. I * ISSUE—3&4 RNI : RAJBIL/2009/30097 Images taken by Phase-Contrast Microscope for identification Result & Discussion temperature and pH, whereas, Mary Bai (1989) reported Physico - chemical parameter that the pH of polluted water fluctuates in the range of The result of Physico - chemical parameters and 8 to 9. The pH value of P1 was near about same the the phytoplankton study of the surface water of two result of Mary Bai. The alkaline pH and reduced water ponds are presented in tables 1, 2, 3 & 4 for level supports the dominance of cyanobacterial species convenience of discussion. The ponds were due to increased photosynthesis activity. represented by P1 (Polsaypara pond) and P2 (Deepak Conductivity of P1 range from 0.88 to1.22 µmhos Nagar pond). Water temperature of P1 were recorded and P2 range from 0.24 to 0.26 µmhos were recorded; ranging from 20.1ºC to 23.1ºC during study period higher value in P2 than P1. Turbidity (NTU) & Total (Table -1); whereas the temperature of P2 (table 2) were Dissolved Solid value was higher in P1 than P2. The recorded ranging from 20.3ºC to 27.2ºC (Table -2). high content of total dissolved solids elevates the Comparatively higher temperature of P2 was due to density of water and such a medium increases the protected by all sides. This high range of osmoregulatory stress on aquatic biota (Verma et al temperature favors the grow of phytoplankton life. 1978). The value of phosphates ranged between 4.17 The pH value of P1 range from 8.63 to 9.25. It was to 5.24mg/l in P2 and 5.44 to 6.35mg/l in P1. It was minimum (8.63) in the month of January and maximum higher value than P2. The higher phosphate value of (9.25) during March 2009. Whereas pH of P2 range P1 could possibly be due to sewage pollution and from 9.05 to 9.65. It was minimum (9.05) in month of human interfere by washing clothes and bathing. January and maximum (9.65) in March. Singhai (1986) Dissolved oxygen in P1 was ranged from 3.3 to 4.2 mg/ has obtained a direct relationship between water l whereas in P2 was ranged from 7.28 to 10.31mg/l. It çÚUâ¿ü °ÙæçÜçââ °‡ÇU §ßñËØé°àæÙ 125
  • 6. International Research Journal ISSN-0975-3486 VOL. I * ISSUE—3 &4 RNI : RAJBIL/2009/30097 was high in P2. The dissolved oxygen almost all plants species Chlamydomonas, Pediastrum, Closterium, and animals need for respiration. Low dissolved Scenedesmus with maximum while Gonium, Pandorina, oxygen creates favorable condition for phytoplankton Tetraedron with minimum occurrence. Chlorella, growth. Biological Oxygen Demand value was recorded Volvox, Oocystis and Ankistrodesmus species were range from 30.4 to 37.4 mg/l in P1 and in P2 it was range recorded occasionally. Among Diatoms Navicula, from 4.3 to 5.7mg/l. This value indicated that the Nitgschila, Fragilaria, Cyndrella, Syrendra, Polsaypara pond (P1) is more polluted than the Deepak Melosira,Gomphonella & Cyclotella species showed Nagar pond (P2).The change in physicochemical maximum density. Among Cyanobactera population, parameters also influence water bodies as it is observed five species namely Arthospira, spirulina were in the present study. recorded maximum density while Phormidium, Phytoplankton composition anabaena anabaenopsis with less frequency and At pond P1 the total number of 26 species of density. Group Euglenophyceae was represented by phytoplankton consisting of 9 species of Euglena and Tracholemons with maximum occurrence. Chlorophyceae, 9 species of Bacillariophyceae, 5 Deepak Nagar Pond: - Group Chlorophyceae species of Myxophyceae and 2 species of included species Chlamydomonas, Pediastrum, Euglenophyceae were identified (Table no. 1). At pond Closterium, Scenedesmus, Pandorina with maximum P2 the total number of 24 species comprising of 6 while Gonium, Tetraedron, Chlorella, Volvox Oocystis species of diatoms, 9 species of Chlorophyceae 5 species were recorded with minimum occurrence. species of Myxophyceae and 3 species of Among diatoms Navicula, Nitzschia & Fragilaria Eulenophyceae and were recorded. At pond P2 species showed maximum density. Among Diatoms were dominated species. Phytoplankton cyanobacterial population Spirulina, & Arthospira population among diatoms such as Cyclotella, were found with maximum density followed by Melosira & Coscinodiscus were found as most Phormidum, Anabaena and Anabaenopsis. Group dominated species. Euglenoidae was represented by Phacus, Euglena and Polsaypara pond: - Group Chlorophyceae included Trachetomonas species. R E F E R E N C E • APHA (1985) Standard methods of the estimation of water, sewage and industrial waste APHA, AWWA, Washington. • Chakrabarty R.O, Roy P and Singh, S.P. (1959) A quantitative study of plankton and the physico- chemical condition of the river Yamuna at Allahabad in 1954-55, Indian J. fish. 6: 186- 203. • Desikachary T.V. (1959) Cyanophyta ICAR, Publication. New Delhi, • Dwivedi B.K. and G.C. Pandey (2002) Physico- chemical factors and algal diversity of two ponds Faizabad India Poll. Res. 21(3): 361-370. • Fritsch, F.E. (1979) The structure and reproduction of the algae. Vikas publishing house Pvt. Ltd. • George, M.G. (1966) Comparative plankton Ecology of five fresh water fish tank in Delhi India. Hydrobiologia. 27: 81-108. • Gleason H.A. (1922) On the relation between species and area Ecology vol.3:156-162 • Goel, P. K., B. gopal R.K. Trivedi (1980) Impact of sewage on fresh water ecosystem. General features of water bodies and sewage Int. J, Ecol. Vol. 17:39:44. • Khan, A. M. (1992) Pysico – chemical characteristics of vishnupuri dam water with special reference to plankton, Ph.D. Thesis, Marathwada University, Aurangabad. • Joseph, J., P N K Nambisan, C. S. Shynamma and P.T. Lakshmanan (1984) Studies on Phytoplankton in polluted waters. J. Mar, Biol. Ass. India Vol. 26 (1&2): 42-46. • Mary Bai, M. (1989) Pollution in polar river physico – chemical parameters in environmental impact on biosynthesis, Eds Proceeding (Vol. 2) of the 10 th annual seminar on Environmental Impact on Biosynthesis at Loyala college, Madras, India. • More Y.S. and Nandan (2003) Hydrobiological study of algae of panzara dam Maharastra Eco. Env. and cons. 9{3) 367-369. • Singhai, S. (1956) Hydrological and ecological studies of newly made Tawa reservoir at Ranipur, Ph.D. Thesis, H.S. Gaur University, Sagar • Sinha Sunju, Naik M.L. (1997) Phytoplanktons and macrophytes in the ponds of Raipur city area.Gupta Offset, Bajrang Nagar; Raipur. • Subrahmanyum, M.N.V. and P.V. Bhavanarayana (1989) Distribution and abundance of phytoplankton in Visankhapatnam harbour Indian J. mar. Sci, Vol, 18: 251-258. • Yoggesh, Shastri, Bharat V. P. and Bhogaonkar (1999) Hydrobiological studies of a Pescolation tank II Algal flora. J. Aqua. Biol. Vol. 14 (1&2) : 1-2. • Trivedi R..K. and P.K. Goel (1986) Chemical and Biological methods for water pollution studies. Environmental Publication. Karad. • Verma, S.R., Tyagi A. R. and Dalella R.C. (1978) Physico – chemical and biological characteristics of Karadabad drain in U.P. Indian J. Environment Health; 20(1) : 1- 13. 126